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首页> 外文期刊>Analytical chemistry >Sampling of Trace Volatile Metal(loid) Compounds in Ambient Air Using Polymer Bags: A Convenient Method
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Sampling of Trace Volatile Metal(loid) Compounds in Ambient Air Using Polymer Bags: A Convenient Method

机译:使用聚合物袋对环境空气中的痕量挥发性金属(类)化合物进行采样的便捷方法

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The sampling of volatile metal(loid) compounds (VOMs) such as hydrides, methylated, and permethylated species of arsenic, antimony, and tin is described using Tedlar bags. Advantages as well as limitations and constraints are discussed and compared to other widely used srm-pling techniques within this area, namely, stainless steel canisters, cryotrapping, and solid adsorbent cartridges. To prove the suitability of Tedlar bags for the sampling of volatile metal(loid) compounds, series of stability tests have been run using both laboratory synthetic and real samples analyzed periodically after increasing periods of storage. The samples have been stored in the dark at 20 “C and at 50 “C. Various volatile arsenic species (AsH3, MeAsH2, Me2AsH, MeaAs), tin species (Sulk, MeSnH3, Me2SnH2, Me3SnH, Me4Sn, BuSnH3), and antimony spe-cies (SbH3, MeSbH2, Me2SbH, Me3Sb) have been gener-ated ~using hydride generation methodology and mixed with moisturized air. Three static gaseous atmospheres with concentrations of 0.3—18 ng/L for the various compounds have been generated in Tedlar bags, and the stability of the VOMs has been monitored over a period of 5 weeks. Sewage sludge digester gas samples have been stored only at 20 “C for a period of 48 h. Cryotrapping GC/ICPMS has been used for the determination of the VOMs with a relative standard deviation of 5% for 100 pg. After 8 h, the recovery rate of all the compounds in the air atmospheres was better than 95% at 20 and 50 “C, whereas the recovery after 24 h was found to be between 81 and 99% for all VOMs at 20 and 50 “C except for Me3Sb and Me3As. These species show a loss between 48 and 73% at both temperatures. After 5 weeks at 20 “C, a loss of only 25—50% for arsine and stibine and the above-mentioned tin compounds was determined. Only MeaSb, Me3Bi, and Me2Te were present in the digester gas sample. After 24 h, losses of 44, 10, aAd 12%, respectively, could be determined. Given these results, Tedlar bags could even be used, with some limitations, for long-term sampling of air containing traces of VOMs. The loss is more pronounced at higher temperatures.
机译:使用Tedlar袋描述了对诸如砷,锑和锡的氢化物,甲基化和全甲基化物质等挥发性金属(类)化合物(VOM)的采样。讨论了优点以及限制和约束,并将其与该领域内其他广泛使用的srm-pling技术进行了比较,这些技术包括不锈钢罐,冷冻捕获和固体吸附剂盒。为了证明Tedlar袋适合取样挥发性金属(胶体)化合物,已经使用了实验室合成的和真实的样品进行了一系列的稳定性测试,这些样品在增加储存时间后会定期进行分析。样品已在20摄氏度和50摄氏度的黑暗条件下储存。各种挥发性砷物质(AsH3,MeAsH2,Me2AsH,MeaAs),锡物质(Sulk,MeSnH3,Me2SnH2,Me3SnH,Me4Sn,BuSnH3)和锑的特性(SbH3,MeSbH2,Me2SbH,Me3Sb已被基因化)使用氢化物​​生成方法并与潮湿空气混合。在Tedlar袋中生成了三种浓度为0.3-18 ng / L的静态气体,用于各种化合物,并且在5周内对VOM的稳定性进行了监测。污水污泥消化池气体样品仅在20摄氏度下存储48小时。低温气相色谱/ ICPMS已用于测定100 pg的VOM,相对标准偏差为5%。 8小时后,在20和50“ C下,空气中所有化合物的回收率均优于95%,而在20和50”下,所有VOM在24 h后的回收率在81%至99%之间。 C,除了Me3Sb和Me3As。这些物质在两个温度下的损失都在48%至73%之间。在20摄氏度下经过5周后,测定出砷化氢和锑化氢以及上述锡化合物的损失仅为25-50%。消化池气体样品中仅存在MeaSb,Me3Bi和Me2Te。 24小时后,可以确定分别损失44、10,aAd 12%。鉴于这些结果,即使有一些限制,Tedlar袋也可以用于长期采样含有微量VOM的空气。损失在较高温度下更为明显。

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